Methods and apparatus for disposing of waste materials



United States Patent Paul G. Marsh Hamilton;

.Earl T. Blakley, Cincinnati, Ohio July 1, 1968 Dec. 22, 1970 The Black Clawson Company Hamilton, Ohio a corporation of Ohio Inventors Appl No. Filed Patented Assignee METHODS AND APPARATUS FOR DISPOSING F WASTE MATERIALS Claims, 1 Drawing Fig.

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Int. Cl. B01d 21/26 Field ol'Search 210/63, 66, 67, 71,73, 152, 170, 178, 179,181, 197,205, 208, 260; 209/10, 11, 238

Primary Examiner-John Adee A trorneys- Marechal. Biebel. French and Bugg ABSTRACT: Waste sludges, particularly sludges resulting from the treatment of municipal sewage, but also including industrial waste sludges, are mixed with the residue obtained by the pulping of garbage, trash and other municipal refuse for the purpose of aiding the conjoint ultimate disposal of both types of wastes. The sludge is mixed with the pulped slurry of municipal wastes in order to take advantage of the ease with which the resulting mixed waste materials can be dewatered to a consistency appropriate for convenient ultimate disposal, especially by incineration in a fluidized bed reactor or other incinerating apparatus.

4e 46 as ea m 55 as V u 26 n PATENTEU UEE22 I970 \u {l} N IN VE N TORS PAUL s. MARSH a EARL T. BLAKLEY W/M Ms A TTUR/VEYS resulting from conventional treatments .of municipal sewage,

provide a continuing and growing disposal problem' for all municipalities. Sewage consists primarily-of wastesfrornresidential, institutional and industrial "t'oilets'baths and sinks, and in somecommunitie's it alsoincludes the output of the storm sewer system. It consists very largely of waterand'dissolved solids, usually in excess of 99percc'nt, with the suspended solids content comprising bothorganic and inorganic constituents,approxirnately one half of which are unstable organic materials subject to 'decaychemical and bacterial metabolism are constantly taking place in sewage, tending to reduce itbyoxidation, f

The process of decomposition of organic matter depends upon the affinity of the particular matterfor oxygen and .the

amount of oxygen which is available: Fresh sewage in which aerobic bacteriaact is relatively odorless because oxygenis still available. Once the available oxygenisexhausted, anaerobic bacteria take over, and cause 'putrification toset in. The sewage is then in a stale condition,- and itbe'gins to giveoff a putrid odor. I

The present methods of sewage treatment and disposal which are mostcomrnonly used'ernploy both the presence and absence of oxygen. The initial step involves settling of raw sewage sludge in a primary sedimentation-tank,wherethe oxygen contained therein yisnearly. exhausted byaerobic digestion. in the further treatment of this settled sludge,it is leather, molded plastics, rubber, garbage, grass and dirt, textransported todigestion-tanks where closely controlledconditions enable anaerobic digestion to reduce it in the-absence of process commonly requires as much as lO to 15 days, and the resulting stable sludge is then dried on open-sand beds or departicularly sludge subject to putrifie'ation, while at the same time minimizing the cost of equipment procedures for this purpose. The invention provides a solution to these several problems through a treatment of waste sludges in combination with municipal refuse which affords outstanding economy and other advantages in the handling'of both types ofwastematerial. I s

The term refuse is a term of art which denotes. indicated for example, in the American Paper Institute Report No. l l4 Sept. I1, 1967, a conglomeration of such diverse materialsas cardboard, newspaper, miscellaneouspaper, plastic film,

tiles, wood, glass, ceramics, stones and metallics, and when used herein it is used in this technically accepted sense. it is not used to denote garbage, which comprises only a fraction of suchrefuse;

The above Baxter application a method and system for effectively converting ahd'rnunicipal refuse, such as garbage and cash, into a pumpable aqueous slurry capable of extraction through a perforate'screen. It has been found in accordance with thepresen't invention that the solid components of the resulting extracted slurry are particularly suited for conditioning undigested sludges for a dewatering treatment to a consistency facilitating their'ultimate disposal. By way of example, tests of the composition of average samples of municipal refuse on an oven dried basis indicate that the slurry produced by treatment asdescribed in the Baxter application'will contain between 7OJand'75 percent of the solid constituents of'the'refuse. Also, more than percent of the solids suspended in the slurry comprise paper products, and an additional 5 percent or morewill consist of wood and other readily combustible material. 1

Sewagesludges constitute a relatively smallproportion of the total of solid wastes requiring disposal by the average municipality, namely of the order of 5 percent. As a result, while the undigested sludge is a gelatinous masswhich is extremely difficult to dewater, when it is mixed witlithe pulped municipal refuse collected for acomparable time period, it conwatered in mechanical thickenersto. a' point at which it can be incinerated, oripe'rhaps used-for fill purposes or as low grade fertilizer. K r 1 Primary sedimentation sludge is difficult to: dewater, because it is an unstable and relatively slimy gelatinous matrix. The process of digesticnby whichit istransformedinto. a

more readily-handled residue'requires not only a-substantial The foregoing comments with respect'to sewage sludges apply also to other types of waste'sludges, whichresult from the operation of a number of industries. For example, a number of metallurgical and chemical processes give rise to sludges having insufficient value to justify any further treatment except incinerationgor some other form of ultimate disposal. The operation'sofpaper mills also give rise to waste sludges which are comparable to sewage sludge in the difficulty of handling and dewat'ering' to a consistency compatible with incineration-or other ultimate disposal,

I SUMMARY or'rue INVENTION l The present invention deals with'two major considerations which are involved in the treatment and disposal of waste sludges. One is the problem of dewatering raw sludge, particularly primary sedimentation sludge,- to a consistency suitablefor incineration, or other subsequent final disposal treatment.

,The invention is also concerned with the provision of 'a fast andefi'icient method of disposing of the dewatered sludge,

stitutes such a relatively small portion of the total as to offer no appreciable resistance to dewatering of the total mass. Conversely, there-is so higha proportion'of fibrous constituents in the total mass, namely morethan SOpercent, that the mass as a whole isrelatively free draining and is not affectcd in this respect by the intermixed sludge.

' There will of course be a significant amount of incombustible material in the extracted slurryprodu'ced in accordance with the Baxter application, particularly-grit such not only as sand and gravel but also glass, ceramics and small pieces of metal. These materials, however, are relatively easily removed to a major extent by conventional cleaning equipment such particularly as centrifugal cleaners, and it is in fact desirable to effect such cleaning before dewatering, particularly if the dewatering is carried out on a vacuum filter or similar equipment filter, screw press, centrifuge or other suitable concentrating apparatus, the removed liquid may be handled in a variety of ways, a particularly useful procedure being to sterilize it and return it to the pulping station as the aqueous pulping medium --therein. The solid "filter cake" produced by the dewatering process, comprising sludge and other solid wastes, is'easily disposed of by incineration in a fluidized 'bed'reactor or other incinerating apparatus. Since this mass includesa large proportion of fibrous materials of highcombustibility, it substantially retains that property even though the added sludge may be somewhat less readily combustible,jand its incinerationwill be essentially self-supporting in that itwill provide sufficient thennal energy to maintain reactor temperature once combustion is startedtherein. In addition, any excess heat producedin-the combustion processcan be utilized for other vpurposes in the practice of theinvention, such particularly as sterilization ofthe liquid removed in dewatering or the heating of the mixed slurry and sludge priorto dewatering.

BRIEF DESCRIPTION OF THE DRAWING The FIG. is a diagrammatic plan view illustrating a complete system in accordance with and for carrying out the method of the invention.

DESCRIPTION OF PREFERRED EMBODIMENTS In the FlG., the apparatus for pulping, compacting and separating the constituents of municipal wastes are shown as comprising a pulper generally of the construction disclosed in the above Baxter application and in Felton and Vokes U.S. Pat. No. 3,339,851, issued Sept. 5, 1967 to the assignee of this application. This pulper includes a tub ll equipped with a rotor 13 mounted for rotation centrally of the bottom portion of the tub in cooperation with a perforate screen plate 15, and

- there is a compartment below the bottom of the tub into which the perforate screen plate 15 transmits particles which have been sufficiently reduced in size to pass through its perforations. For preferred practice of the invention, these perforations are of relatively small size, preferably of the range of lainch to one inch diameter, and the slurry passing therethrough is withdrawn from the pulper by the conduit 16.

As described in the Baxter application, municipal wastes and water are delivered continuously or intermittently to the pulper tub l1, and the construction and operation of the pulper produce maximum forces of hydraulic shear in its contents, causing defibering of the paper waste material and disintegration of other wastes, both organic and inorganic. The rotor also has a mechanical action which combines with the hydraulic action to reduce the size of nondegradable waste, such as metal cans, by striking them with such force as to have the efiect of rolling them into balls, and the same action causes glass bottles and other frangible materials to be quickly broken into multiple small fragments. Other metal wastes of larger sizes are also rapidly compacted, while the vertical action in the tub causes wires and other stringy or nonfibrous sheet materials to be wound into a ropelike form for ready removal from above.

Provision is made for removing each of these two classes of solid waste from the tub 11 separately from each other and from the pulpable slurry which passes through the screen 15 into the conduit 16. The stringy materials are removed by a tagger as disclosed in the Baxter application and in Cowles US. Pat. No. 2,340,511 issued Feb. 1, 1955. The compacted metal and other hard material of too large particle size to pass through the screen plate 15 are'separated from the slurry in the tub by gravity with the aid of a continuous junk remover 22, also as described in the Baxter application.

The FIG. illustrates the application of the invention to a complete system for continuous processing of municipal sewage sludges and solid wastes, in which the pulper 10 of the characteristics already described is the primary apparatus. It receives the solid waste continuously or intermittently from a conveyor 25, and it is also provided with a continuously available supply line 26 of fresh water for wash-up purposes, and also for initial charging of the pulper if desired.

The pulper l0 progressively reduces as much as possible of the solid wastes to a slurry form, and since the paper content of average municipal wastes now approaches 50 percent, approximately 50 percent of the particles in the slurry will be fibers. The balance will be of varied nature, ranging from organic materials derived from garbage and human waste to hard particles which can generally be grouped under the heading grit." All of this material will be delivered to the conduit 16 as soon as it is of sufficiently small particle size to pass through the perforations of screen 15.

The FIG. also shows schematically a standard sewage treatment plant for efiecting sedimentation of sewage sludge and clarification of effluent, comprising a primary sedimentation tank 30, an aeration tank 31, and a final sedimentation tank 32, all in series. Sanitary sewage from main sewage line 33 passes through primary sedimentation tank 30 where its flow rate and detention time determine the percentage removal of solids from the infiuent. These solids settle to the bottom of tank 30 in the form of sewage sludge, and the effluent is delivered through line 35 to aeration tank 31.

A line 36 supplies compressed air to the liquid in aeration tank 31 in order to suppress anaerobic decomposition and to remove dissolved or suspended solids therefrom. The liquid is delivered through line 37 to the final sedimentation tank 32 where a flocculent precipitate, called activated sludge, settles out to leave a clear, odorless effluent. For proper results, some of this precipitate is recycled to tank 31 through line 41 for seeding purposes. Excess activated sludge is recycled to primary tank 30 through line 42. The clarified effluent from tank 32 may be chlorinated or otherwise chemically treated.

In present practice, the waste sludge from primary sedimentation tank 30 is transferred to an enclosed insulated tank where anaerobic digestion takes place free from contact with atmospheric oxygen. However, the process of anerobic decomposition requires ten to fifteen days, its initial equipment cost is high, and it requires special maintenance and supervision. In accordance with the present invention, the digestion apparatus and operation are eliminated, the sludge is mixed directly withthe slurry of other wastes, and the resulting mixture of sludge and slurry is then processed for ultimate disposal.

In the preferred practice of the invention, the sludge is mixed with the slurry which has been extracted from the pulper l0, and this is represented in the FIG. by a mixing tank 45 to which the slurry and sludge are delivered by the conduit 16 and a line 46 from the pulper l0 and sedimentation tank 30 respectively. Alternatively, the sludge can be delivered directly to the pulper, as indicated by the line 48, for pulping with the other wastes, or added to the refuse prior to delivery of both constituents by conveyor 25 to the pulper. However, these methods of mixing will result in contamination of themsoluble hard materials which are removed by the junk remover 22, and may therefore require a more thorough washing than that provided in junk remover 22 before they are further handled. In either event, the system as shown will ultimately provide in the mixing tank 45 a suspension comprising the extracted waste slurry produced in the pulper l0 and the sludge from the sedimentation tank 30. 1

In the average municipality the sludge produced by the sanitary sewage system amounts to a relatively small proportion of the total solid waste requiring disposal, for example of the order of 5 percent. Therefore, even if all of the sludge produced during a given period is mixed with the slurry produced by treatment in the pulper 10 of the solid wastes collected for the same time period, the amount of sludge will still be minor in comparison with the amount of fibrous material,

particularly the cellulose fibers produced by pulping of the large amount of paper products found in municipal trash and garbage. The invention takes major advantage of this mixture of materials in its further treatment thereof, and in particular it takes advantage of the fact that with the relatively gelatinous sludge mixed with the much larger quantity of fibrous constituents of the slurry, the resulting conglomerate is easily concentrated to comparatively solid consistency by conventional filtering or other dewatering apparatus.

Thus in the FIG., the mixture of extracted slurry and sludge is shown as pumped from the mixing tank 45 by a pump 50 to suitable grit removers, shown as a plurality of liquid cyclones 55 connected in parallel for the removal of high specific gravity gritty material. This step is not necessarily essential to'the success of the invention, but it is highly desirable, particularly if the dewatering is to be carried out by a vacuum filter, since other wise the filter would be subject to unnecessary damage if the gritty materials are allowed to remain in the slurry. The accepted material from the cyclones 55is accordingly shown as being delivered to any appropriate means, 60 for dewatering, and as oneexample, the invention may be readily practiced by means of e a vacuum filter 60 of. conventional construction, which is capable of increasing the solids content of the'slurry frornless than 11 to 30 or.more.0ther dewatering means such l as a screw press or centrifuge may be used, particularly when a .higherjdegreeof concentration is desired, and it is also possible to combine the stepof'mixing the sludge and slurry with the dewatering step, for example by adding sludge to the slurry asavacuum filter. L The products of the dewatering; operation, namely filter cake and removed liquid, may be handled. in various ways. One aspect of the invention takes particular advantage of the fact thatthe dewatering can readily be carried to a point at which the resulting filter cake is capable of sustaining its own combustion, due to the large proportion of fibrous constituents, and this resultcan be achieved with a solids content of the order of 25 percent or more; This isillustrated in the FIG. by the provision of a conveyor'65, such as a screw feeder, connected between the dewate'ring apparatus 60 and asuitable incinerator 6 6. ,Al ternatively, the'filter cake may be used cfor'otherapurposes such as composting or the like, but becauseit. comprises relatively combustible wastes 'of low value, it is most conveniently disposed of by incineration. Theremoved liquid, which will still contain suspended and disspecific type of incinerator, highly satisfactory results are ob-' tained if the incineration is carried outin a fluidized bed reactor, particularly because of the completeness of disposal and simplicity of operation of this type of incinerator as compared,

for example, with multiplehearth arid flash-type incinerators.

The incinerator-W6 in. the FIG. isaccordingly shown as a fluidized bed reactor, body 70 of cylindrical: configuration which includes a tapered lower portion in which an orifice plateorgratei 71-supports the bed-7 z of particles of sand,

'stoneorthelike.:'- =::r?- v lnoperatiori', the particles which comprise the bed' 72 are preheated by suitable heating means (not Shown) to a relatively'higlr temperature, e.g.' 1500F., and air is blown upward through the orifice plate 71 to fluidize the] bed 72, as indicated by the blower-75. The filter cake from-the filter 60 is delivered by the conveyor 65tothe top of the body 70 for downward delivery thereto, and it is desirable tobreak up the filter cake as it is .delivered by means such as a jet of air introduced as indicated bythe nozzle 77. The filter cake is initially incinerated by contact with the heatedparticles of the fluidized bed, and the high proportion of fibers and other readily flammable materials in the filter cake thereafterv continue to support the combustion andto maintain the heat of the fluidizedbedparticles sufficiently so than use of the external heat source may be discontinued.

The relatively small residue of ash produced in the fluidized said aqueous medium from said mixed sludge and refuse com- 7 vention contemplates that with this arrangement, the removed 1 liquid may be heated to the point of sterilization beforeit is reused for pulping purposes; thereby contributing both to sanitation and to the ease of pulping-and the subsequent dewatering of the extracted slurry from the pulper.

An alternative way of utilizing the heat generated by the incinerator 66 is for preheating the extracted slurry from the pulper 10 before it is dewatered l-le at left over from heat exchanger may be directed for this purpose through lines 84 and 86 to heat exchanger 88, or, alternatively, the heat from incinerator 66 may be directly administered to the mixed slurry from flue 81 through line 86. Such preheating will provide one or both of two significant advantages, namely increased ease of dewatering, especially by a vacuum filter, and also sanitation if the heating is carried to the point of sterilization. It is of course'apparent that any of these heating steps can be carried out by heat obtainedfrom' another source, and also that sterilization can be effected by the addition of a suitable sterilizing agent, e.g. a chlorine, but the economics of the system and process are enhanced when disposition of the wastes is by incineration, and the heat produced by such incineration is reused in the system.

While the methods and forms of apparatus herein described constitute preferred embodiments of the invention, it is to be understood that the invention is not limited to these precise methods and forms of apparatus, and that changes may be made therein without departing from the scope of the invention which is defined in the appended claims.

Weclaim: M

l. A method of treating waste material comprising: 7

a. depositing ina waste treatment tub an aqueous medium I and refuse including;

i. a relatively high proportion of fibrous and other organic materials with the percentage of said refuse constituted by said fibrous material being greater than the percentage of said refuse constituted by any other component thereof, and

ii. glass, metal and other inorganic materials,

b. subjecting said refuse to comminution to reduce at least said fibrous material to at least'a predetermined particulate size: a I

c. extracting from said tub in slurry form refuse below said predetermined particulate size and some of said aqueous medium: I

d. mixing sludge with said refuse; and q I e. subsequent to said extraction, removing a substantial portion of said aqueous medium from'said mixed sludge and 2. The method of claim 1 wherein; said sludge is mixed with said refuse prior to deposition thereof in said waste treatment tub.

3. The method of claim 1 wherein; saidsludge is mixed with said refuse in said waste treatment'tub.

4. The method of claim 1 wherein; saidsludge is mixed with said refuse subsequent to said extraction of said refuse in said slurry form from said tub.

5. The method of claim 1 wherein; sludge is mixed with said refuse concurrently with dewaten'ng of said refuse in said slurry form.

6. The method of claim 1 wherein; said fibrous material comprises approximately 50 percent of said refuse.

7. The method of claim 1 wherein; said fibrous material comprises in excess of 50 percent of said 8. The method of claim 1 wherein; sludge comprises approximately 5 percent of the total of said refuse and said sludge.

9. The method of claim 1 wherein; said step of removing prises removing said aqueous medium from saidmixed sludge and refuse until the resulting mass is capable of supporting combustion.

10. The method of claim 9 wherein said step of removing said aqueous medium from said mixed sludge and refuse is continued until the solids content of the resultant mass is in excess of 25 percent.

material and said refuse in slurry form.

14. The method of claim 1 further comprising; returning said aqueous medium removed from said mixed sludge and refuse to said waste treatment tub.

15. The method of claim 14 further comprising; subjecting said aqueous medium removed from said mixed sludge and refuse to sterilization prior to its return to said waste treatment tub. 

